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Waste Minimization and
Cleaner Production
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Introduction In the last 15 20 years there has been a growing world
wide movement among government and industry to changethe way industry interacts with the environment.
The focus of this movement has been to reduceenvironmental impacts from industry through changes inindustrial behavior and technology.
All of them are based on what is commonly known as theprecautionary Principle, also known by the old saying,
An ounce of prevention is worth a pound of cure.
It is better, and usually much less expensive, to preventenvironmental problems from happening than to fix themonce they are created.
And if we dont know what effects our actions will have onthe environment, we should proceed with caution and try tominimize any potential effects that might occur.
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Objective
The objective of this lecture is to briefly define the mostcommon concepts used for industrial environmentalmanagement and to show their relationships.
There are many actions industry can take, from the
small to the very large, along a path orstaircase thatleads to increasingly broad impacts on and interactionswith the environment and society.
No industry, and no society, is really at the top of thestaircase; the top, which is sustainable development, is,like quality, a goal which is always elusive and for whichwe should never stop striving.
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The Staircase of Concepts In IndustrialEnvironmental Management
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Concept of Stair Case
There are three types of concepts on the staircase.
(1)Macro-scale concepts:
The macro-scale concepts ofsustainable development and industrialecology extend far beyond the firm and include relationships betweencompanies, social institutions, the public and the environment in all its facets.
(2) Firm-wide concepts:
The firm-wide concepts of environmental management systems and cleanerproductionaddress all aspects of the firms operations, from use of naturalresources to suppliers to production to product use to product disposal.
(3) Operational concepts:
The remaining operational concepts address specific functions of the
business.
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Macro-Scale Concepts
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Sustainable Development
Sustainable development is the development that meets the
needs of the present without compromising the ability of futuregenerations to meet their own needs
It contains within it two key concepts:
The concept of "needs", in particular the essential needs of the world's poor, towhich overriding priority should be given; and
The idea oflimitations imposed by the state of technology and social organizationon the environment's ability to meet present and future needs.
Thus the goals ofeconomic and social development must be defined in terms ofsustainability in all countries -- developed or developing, market-oriented or centrally
planned.
Interpretations will vary, but must share certain general features and must flow from a
consensus on the basic concept of sustainable development and on a broadstrategic framework for achieving it.
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Industrial Ecology
Industrial ecology is the means by which humanity candeliberately and rationally approach and maintain adesirable carrying capacity, given continued economic,cultural and technological evolution.
The concept requires that an industrial system be viewednot in isolation from its surrounding systems, but in concertwith them.
It is a system view in which one seeks to optimize the totalmaterials cycle from virgin material, to finished material, toproduct, to waste product, and to ultimate disposal.
Factors to be optimized include resources, energy and
capital
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Aim of Industrial Ecology
The aim of industrial ecology is to interpret andadapt an understanding of the natural systemand apply it to the design of the man-madesystem, in order to achieve a pattern ofindustrialization that is not only more efficient,but that is intrinsically adjusted to the tolerancesand characteristics of the natural system.
The emphasis is on forms of technology that workwithnatural systems, not againstthem...
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Firm-Wide Concepts
These are concepts that affect the whole scope of the business enterprise, not just
parts of it.
They are essentially management philosophies and practices rather than technical
practices and as such are best directed to the top levels of management.
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Cleaner Production
Cleaner production means the continuous application of an integratedpreventive environmental strategy to processes and products to reduce risks
to humans and the environment.
For production processes, cleaner production includes conserving raw materials
and energy, eliminating toxic raw materials, and reducing the quantity and toxicity of
all emissions and wastes before they leave a process.
For products, the strategy focuses on reducing impacts along the entire life cycleof the product, from raw material extraction to the ultimate disposal of the product.
Cleaner production is achieved by applying know-how, by improving technology,
and by changing attitudes.
The conceptual and procedural approach to production that demands that all
phases of the life-cycle of products must be addressed with the objective of the
prevention or minimization of short and long-term risks to humans and the
environment.
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Pollution Prevention
The USA Pollution Prevention Act of 1990 defines pollution prevention as a
goal which is realized through source reduction.
The term ''source reduction'' [or pollution prevention] means any practicewhich
Reduces the amount of any hazardous substance, pollutant, orcontaminant entering any waste stream or otherwise released into the
environment (including fugitive emissions) prior to recycling, treatment,or disposal
Reduce the hazards to public health and the environment associated withthe release of such substances, pollutants, or contaminants
The term includes equipment or technology modifications, process orprocedure modifications, reformulation or redesign of products,substitution of raw materials, and improvements in housekeeping,maintenance, training, or inventory control.
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Operational Concepts
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Why Waste Minimization ?
The generation of large volumes of waste correlates with
the depletion of mostly non-renewable resources
The energy requirement for the transformation and
upgrading of wastes is in proportion to the quantities treated
and rises exponentially with increasing dilution of the waste
The increasing total costs for collection, segregation,
intermediate storage, transport etc.
Increased public and legislative pressures seem likely to do
mitigated only by waste reduction/minimization
Since waste equals inefficiency, reducing waste increases
efficiency and hence profitability
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Waste Minimization
Waste Minimization (WM) is the reduction, to the extent feasible, of hazardous
waste that is generated or subsequently treated, sorted or disposed.
It includes any source reduction or recycling activity undertaken by a generator
that results in either
(1) The reduction of total volume or quantity of hazardous waste, or
(2) The reduction of toxicity of hazardous waste, or both, so long as such
reduction is consistent with the goal of minimizing recent and future threats to
human health and the environment.
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Clean Technology
It has two ideas
1. The emphasis is on the generation of less waste and onthe consumption of fewer raw materials and less energy.Thus a simple but satisfactory definition of cleantechnology is any technology or process which uses
fewer raw materials and/or less energy, and/or generatesless waste than an exiting technology or processes.
2. The avoidance of end-of-pipe emission reduction is alsoemphasized. End-of-pipe methods are those that attemptsto reduce the environmental impact of a waste, after thatwaste has been produced.
Th t f i i h b
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The concept of zero emission processes has beenespoused, such a target is thermodynamically impossiblefor a manufacturing processes, if such processes isregarded as an open system (a system that exchangesboth material and energy with its surroundings).
Manipulating the system boundary in an attempt toproduce a closed system (One that exchanges only
energy and not materials with its surroundings) isanalogous to the end-of-pipe solutions to materialproblems, which merely transfers matter from onemedium to the other.
Enlarging the systems boundary to incorporate theenergy supply facility reveals that the enlarged system isin fact, open and depositing material into thesurrounding.
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What is life cycle assessment ?
It is a systematic inventory and comprehensive assessment of environmental effectsof two or more alternative activities involving a defined product in a defined space
and time including all steps and co-products in its life cycle.
Any product may have following stages in its life cycle
Raw materials acquisition
Bulk material processing
Engineered and specialty material production
Manufacturing and assembly
use and service
Retirement Disposal
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Product life cycle system (from Koelein and Menerey, 1993)
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Steps Necessary to conduct a Life Cycle Assessment
An LCA has the following phases:
Planning Screening
Data collection (inventory) Data treatment (aggregation/classification) Evaluation
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(material down scaling into another product system)
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West Reproduction Technique
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Thermodynamics and Material Flows in the Economy
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Transformationprocess
Material inputs
Energy inputs
Wastes & emissions
Useful outputs
Thermodynamics and Material Flows in the Economy
1. Law of Thermodynamics:Conservation of energy
In non-nuclear processes energy can neither be created nor destroyed. Energy can onlybe transformed from one form into another. The total amount of energy input to a non-
nuclear transformation process is thus equal to the total amount of energy output.
Conservation of massThe total mass of material inputs into a (non-nuclear) material transformation process is
equal to the total mass of material outputs.
Conservation of mass per chemical elementThe total mass of each chemical element is conserved during every (non-nuclear)
material transformation process.
The material transformation process
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afterbefore
outputinput
emissionswastesproductsancillarydirect
EntropyEntropy
EnergyEnergy
MassMassMassMassMass
Direct materials
Ancillary materials
Low-entropy energy
Economic output
Wastes & emissions
High-entropy energy
Transformation process
1. Law of TD
2. Law of TD
e ate a t a s o at o p ocess
Solar Radiation Earths RadiationMaterial Flows in the Economy
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Ecosphere
Anthroposphere
Materials
Sink for:
Wastes
&Emissions
Needs & Wants
(Teff~ 6000K
mainly UV, optical and IR)(Teff~ 300K
mainly IR)
Services
Products
Production
All materials that enter the economic system will eventually leave it
Large amounts of low-entropy energy are needed to drive the economic system
All economic activity is essentially dissipative in both materials and/or energy
Low-entropyEnergy
Material Flows in the Economy
high-entropy
Energy
Material Flow Analysis (MFA)
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Accounting methodology for material stocks:
Producing
processes
Imports Exports
Consuming
processes
Stocks of
upstream
materials
Stocks of
downstream
materials
Stocks outside
of boundaries
Stocks outside
of boundaries
Material
stock
Transformation processes
Transportation processes
lllll
tt
ExportImportnConsumptioProductionStock
tdExportImportnConsumptioProductionStockdStock
Methodology Single material or substance
MFA Methodology Single material or substance
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Material
production
Potential
Waste
Component
fabrication
Product
Assembly
Product
Use
Raw
Material
Material Components Products
Imports / Exports
Domestic Environment
Extraction ReleaseRecycling Reuse
Example: Copper Flows in North America in 1994 (in kt / y)
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Import / Export
EnvironmentLithosphere
Production:
Mill, Smelter,
Refinery
Fabrication &
Manufacturing
Use Waste
Management
Concentrate,
Blister, Cathode
325
Ingots
3
Semis,
Finished Products
17
Stock
Cathode
3270Prod. Cu
2640
Prod. Alloy
690
Stock
1920
Discards
1410
Old
Scrap
190
New Scrap
730140
Old Scrap180330
Tailings & Slag 365
Ore
3130
Landfilled Waste,
Dissipated
Source: CIE, Yale
710
3
Recycling
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Recycling
There are almost always some wastes created by production processes, so they
need to be recycled as much as possible. Recycling can be broken down into
closed-loop recycling (which is really just a production process extension rather
than recycling), on-site recycling and re-use, off-site recycling, and reclamation.
Common Effluent Treatment Plants
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Leachate collection and ewaporation pond
at the common facility for waste
management at Hyderabad (A.P.)
Common Effluent Treatment Plants
Oxidation Pond based Treatment Plant
at Vrindavan, UP
Pollution Control
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Pollution Control
Pollution control systems to reduce waste volume or toxicity are a necessityto manage wastes that cannot be prevented or exchanged. The relationship
to the higher concepts is one of fast resort
Waste Disposal
A view of hazardous waste storage pits
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Indian Scenario
Hazardous Wests Generating Units &
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g
HW Generation Scenario
HW generation in States - No uniform trend No. of Units generating Hazardous Wastes gone-
up
Factors responsible:
Changes in regulatory classification:o Change over from 18 waste categories with
annual threshold limits to 36 processes and
corresponding waste streams
o Emphasis on waste minimization-zerodischarge(Tanneries,textiles)
o Fly-ash,gypsum sludge excluded
o Units closed/New Units
Waste Stream wise Quantification of Hazardous Wastes
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Product Waste Stream WGF (kg/tonne of product)
Ethylene/Propylene Spent caustic from CausticTower
0.06
Oil Soaked Carbonaceous Coke 0.017
Spent Palladium Catalyst 0.007
Butadiene Butadiene Polymer Waste 0.06
Solvent regeneration residue 0.4
Benzene Spent Nickel Catalyst 0.03
Spent Nickel-MolybdenumCatalyst
0.003
Spent Cobalt-MolybdenumCatalyst 0.007
Waste Stream wise Quantification of Hazardous Wastes
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Product Waste Stream WGF (kg/tonne of product)
Xylene Spent clay 0.50
Vinyl ChlorideMonomer
Carbon Waste 0.02
EDC Bottom Viscous 4.0
Reactor Waste 0.014
Polyvinyl Chloride PVC Wet resin 4.0
Ethylene Oxide/Ethylene Glycol
Spent Silver catalyst 0.08
Polythylene Polymeric waste 0.02
Extruder waste 2.4
Maleic anhydride Distillation bottoms 60
ETP sludge 0.4
Waste Stream Contd. ..
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Product Waste Stream WGF (kg/tonne ofproduct)
Phthalic Anhydride Vanadium pentoxide catalyst 167
Purge cut 24
Tar residue 12
Dimethyl Terephthalate Crude ester distillation residue 54
Linear Alkyl Benzene Calcium fluoride sludge 6.0
Spent alumina 0.32Spent catalyst 0.04
Spent molecular sieve 0.35
Spent carbon 0.02
Oil soaked sand 0.8
Isopropyl Alcohol Spent copper catalyst 45.0
Acetone Distillation by product (Tarry waste) 8.0
Petrochemical Industry : Suggested Waste Recycling Options
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Product Waste Recycling Measures
Ethylene/ Propylene Polymeric waste Refining and reuse
Benzene Spent nickel catalyst Metal recovery
Spent nickel-molybdenumcatalyst
Metal recovery
Spent cobalt-molybdenum
catalyst
Metal recovery
Polyvinyl chloride PVC wet resin Reuse for manufacturinguseful items
Isopropyl alcohol Spent copper catalyst Recovery of acid
Acetone/Phenol Solvent waste Use as a fuel in the boiler
Polypropylene Powder waste Melting, extrusion andconversion to low-gradearticles
Cumene Cumene catalyst Acid recovery
Cumene bottoms Use as a fuel
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HW Generating Industries & HW Generation
C ti Fi
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S.No. State No. ofIndustriesas per HWM
Rules, 1989
Total HWgeneration inTPA
HW generatingIndustries(No.s) as per
HWM Rules,2000/2003
Total HWgenerationin TPA
1. AP 501 1,11,098 1532 507046
2. Assam 18 1,66,008 23 4,000
3. Bihar 42 26,575 31 Not given
4. Chandigarh 47 305 271 8,4255. Delhi 403 1,000 1777 17,000
6 Goa 25 6,598 49 Not Provided
7. Gujarat 2984 4,30,030 6052 12, 07,000
8. Haryana 309 31,046 889 14,972
9. Himachal 116 2159 575 Not given10. Karnataka 454 1,03,243 1589 92,013
11. Kerala 133 1,54,722 423 83,530
12. Maharashtra 3953 20, 07,846 4571 14,07,480
13. MP 183 1,98,669 753 Not given
14. Orissa 163 3,41,144 257 74,918
Comparative Figures
HW Generating Industries & HW Generation
C ti Fi
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S.
No.
Name of theState
No. ofIndustries asper HWM
Rules, 1989
Total HWgeneration inTPA
No. of HWIndustries asper HWM
Rules,2000/2003
Total HWgenerationin TPA
16. Pondicherry 15 8,893 66 30,320
17. Punjab 700 22,709 1448 15,769
18. Rajasthan 332 1,22,307 512 1,83,737
19. Tamilnadu 11003,94,208
2177 1,81, 624
20. Uttarpradesh 1036 1,45,786 1633 82,375
21. West Bengal 440 1,29,826 568 Not given
22 Chattisgarh - - 149 Not given
23. Mizoram - - Nil Nil
24. Meghalaya - - 39 37, 41225. Nagaland - - 03 448
26. Daman, Diu &DNH
- - 598 Not given
27. Jharkhand - - 169 Not given
28. Uttaranchal - - 137 Not given
29. Manipur - - Nil -
Comparative Figures
STATE-WISE COMPARATIVE HW GENERATING UNITS AS
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PER HWM RULES, 1989 & 2003
309
47
116133
183 163
57
271
889
575
423
753
257207
0
100
200
300
400
500
600
700
800
900
1000
Chandigarh
Haryana
Hima
chal
Ke
rala
MP
Or
issa
J
&K
STATE
No.
ofHWg
eneratingUn
its
HW generating Units as per HWM RULES, 1989
HW generating Units as per HWM RULES, 2003
Comparative HW generating Units as
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501
1532
2984
6052
454
1589
3953
4571
700
1448
1100
2177
1036
1633
0
1000
2000
3000
4000
5000
6000
7000
AP
Gujarat
Karnataka
Mahara
shtra
P
unjab
TN
UP
State
perHWM Rules, 1989 and 2003
No. of HW units as per HWM Rules, 1989
No. of HW units as per 2003
HWs - Landfillable, Recyclable,
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650
410
147
230
264
126
626
628
154
56 109
0
200
400
600
800
1000
1200
1400
1600
Guja
rat
AP
Ma
haras
htr
Oris
sa
State
Incinerable as per HWM Rules, 2003
Landfillable Recyclable Incinerable
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S No State Total HW No of TSDF in No of sites No of sites
Status on HW Generation & TSDF in Operation in Major States
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S.No.
State Total HW
generation in
000 TPA
No. of TSDF inoperation/underconstruction
No. of sites
notified
No. of sites
identified
1. AP 507 01 02 02
2. Assam 4 - - -3. Chandigarh 8 - - -
4. Delhi 17 Nil Nil 03
6 Goa - Nil Nil Nil
7. Gujarat 1207 07 16 22
8. Haryana 15 - 01 01
9. Himachal - - 02
10. Karnataka 92 Nil 02 02
11. Kerala 84 Nil 01 01
12. Maharashtra 1407 02 02 06
13. MP - Nil Nil 03
14. Orissa 75 Nil 01 0115. Pondicherry 30 Nil Nil Nil
16. Punjab 16 Nil 01 01
17. Rajasthan 184 Nil 01 08
18. Tamilnadu 182 Nil 01 03
19. Uttarpradesh 82 Nil 03 05
Common TSDFMulti State
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Flexibility for Industries located on Inter
State Border
Problem facing smaller States/UTs
Incinerable wasteMin. Scale of operation
- about 1.0 ton per hour
Practical Difficulties: Delhi, Chandigarh,
Daman, Goa
Incinerable HW as per HWM Rules 2003
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9.3 12.6
61.4
147 154
02040
6080
100120140160180
Orissa
AP
UP
Gujarat
Maha
rashtra
State
IncinerableHWin
'000
Tonnes
Incinerable HW as per HWM Rulex, 2003
Recycling of Hazardous Waste
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Import of specified categories permitted for Recyclingusing environmentally sound technology
Recycling of hazardous waste is permitted for unitsregistered with CPCB and having ESM Facilities.
Guidance Document prepared on ESM of followingRecyclable wastes : Used Oil, Waste Oil, Non-ferrousmetals wastes
Technology Up gradation: linked to scale of operation
Large Gap between Demand and Supply w.r.t Lead ,Copper and Zinc wastes.
India favours free movement of recyclables.
Recycling of Hazardous Waste contd
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Recyclable Wastes for which State of Art Facilities areneeded
Mercury Bearing wastes.
Nickel Cadmium Batteries
Spent Catalyst
E- Waste:
Guidance document under preparation covering
i ) Informal sectorii ) leaded glassiii) precious metals recovery etc.,
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